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Fen Management Handbook - Scottish Natural Heritage

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10.3.3 Vegetation Mapping<br />

An initial identification of the plant communities present in a fen, with approximate<br />

mapping of the community boundaries, is crucial for identification of key species<br />

and informing the understanding of physical mechanisms affecting a site. This is<br />

usually based on a survey using the NVC methodology (Rodwell J. S. ed. 1991 –<br />

2000).<br />

The NVC methodology is both rigorous (i.e. careful application of the method will<br />

yield consistent and reliable results) and robust (i.e. it is not sensitive to minor<br />

differences in technique). However, it is a plant community classification method,<br />

not a mapping or monitoring method. The recording method is based on selecting<br />

locations for quadrats that appear typical of the community that is being observed,<br />

well within the boundaries of that apparent community.<br />

A set of NVC quadrats can provide an almost complete species list for a defined<br />

area, which can be quickly completed by a check for other species outside the<br />

quadrats, using the DAFOR abundance scale. This can provide the basis for the<br />

qualitative monitoring of the community in that part of the site.<br />

Basic fen monitoring techniques<br />

Quadrats are square frames (usually 4 square metre (2x2m) on fens)<br />

used to sample vegetation. The presence of plant and moss species and<br />

their relative density or abundance is recorded within the quadrat. The<br />

location of the quadrat is described with a GPS, or marked with a post,<br />

so that the vegetation can be re-surveyed and described repeatedly at<br />

the same location in future to detect changes. Further information on<br />

quadrat methodology can be found in Ecological Census Techniques<br />

(Sutherland, 2006).<br />

Transects, or lines, are used to sample vegetation along a gradient<br />

or gradual change of the vegetation. The transect can be up to 100<br />

m long or more, the length depending on the changes or gradient to<br />

be monitored. Vegetation is normally sampled with a quadrat at fixed<br />

intervals, say every 5 m, along the transect, or where tall vegetation (such<br />

as reed encroachment) or abiotic changes (such as change in slope,<br />

groundwater seepage zone) occur. The environment is also normally<br />

measured along the same transect so that changes in vegetation can be<br />

correlated to changes in the environment, and vice-versa.<br />

Advantages of vegetation community mapping and survey include:<br />

– The NVC methodology can provide a clear and rigorous description of the plant<br />

communities present on the site.<br />

– A set of well recorded NVC quadrats can provide useful species presence and<br />

abundance data for a defined location.<br />

– Where well-defined, boundaries between communities can be accurately mapped<br />

using appropriate techniques.<br />

– Two sets of data are generated; geographical data for the community extent and<br />

qualitative data for the community composition in a particular area of the site.<br />

– The data can be presented graphically, as readily comprehensible maps.<br />

– GIS mapping gives precise measurement of areas, allowing changes to be quantified.<br />

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